6b 4 attach 2 reduced

Item No.      6b_attach_b 
Date of Meeting: November 22, 2016










April 2016 
PORT OF SEATTLE 
Implementation Plan 
Seattle-Tacoma International Airport
Flight Corridor Safety Program 
Prepared by 
Anchor QEA, LLC 
720 Olive Way, Suite 1900 
Seattle, Washington 98101

IMPLEMENTATION PLAN 
SEATTLE-TACOMA INTERNATIONAL 
AIRPORT FLIGHT CORRIDOR SAFETY
PROGRAM 

Prepared for 
Port of Seattle
P.O. Box 68727
Seattle, Washington 98168

Prepared by 
Anchor QEA, LLC
720 Olive Way, Suite 1900
Seattle, Washington 98101
Graphics originated by Port of Seattle

April 2016

TABLE OF CONTENTS 
1  INTRODUCTION ................................................................................................................ 1 
1.1   Components of Implementation Plan ..............................................................................1 
1.2   Overview of Port, Public, and Private Sites .....................................................................1 
2  OBSTRUCTION INVENTORY ............................................................................................ 4 
3  OBSTRUCTION REMOVAL AND SITE MANAGEMENT METHODS ............................. 6 
3.1   Site Preparation .................................................................................................................6 
3.2   Tree Obstruction Removal and Material Disposal...........................................................8 
3.3   Site Treatment..................................................................................................................13 
3.4   Monitoring .......................................................................................................................16 
3.5   Erosion and Sediment Control Best Management Practices.........................................17 
4  SITE PLANS ....................................................................................................................... 19 
4.1   Port Properties .................................................................................................................20 
4.2   Public Properties..............................................................................................................50 
4.3   Private Properties ............................................................................................................58 
5  SCHEDULE ........................................................................................................................ 69 
5.1   Overall Schedule..............................................................................................................69 
5.2   Sequencing by Site...........................................................................................................69 
6  REFERENCES .................................................................................................................... 70 

List of Tables 
Table 2.1       Obstruction Removal Summary by Location..................................................5 
Table 3.2-1      Summary of Obstruction Removal and Clearing Methods ............................9 
Table 3.2-2      Summary of Material Disposal Methods .......................................................12 
Table 4.1-1      Summary of Tree Removal and Replacement Quantities  All Sites...........19 
Table 4.1-2      Summary of Tree Removal and Replacement  Port Sites ...........................20 
Table 4.1-3     Port Site P-1 Obstruction Summary ..............................................................22 
Table 4.1-4     Port Site P-1 Best Management Practices .....................................................25 
Table 4.1-5     Port Site P-2 Obstruction Summary ..............................................................27 

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Table 4.1-6     Port Site P-2 Best Management Practices .....................................................30 
Table 4.1-7     Port Site P-3a Obstruction Summary ............................................................33 
Table 4.1-8     Port Site P-3b Obstruction Summary............................................................33 
Table 4.1-9     Port Site P-3 Best Management Practices .....................................................36 
Table 4.1-10    Port Site P-4 Obstruction Summary ..............................................................38 
Table 4.1-11    Port Site P-4 Best Management Practices .....................................................40 
Table 4.1-12    Port Site P-5 Obstruction Summary ..............................................................42 
Table 4.1-13    Port Site P-5 Best Management Practices .....................................................45 
Table 4.1-14    Port Site P-6 Obstruction Summary ..............................................................46 
Table 4.1-15    Port Site P-6 Best Management Practices .....................................................49 
Table 4.2-1      WSDOT Site WP-1 Obstruction Summary...................................................51 
Table 4.2-2      SeaTac Site SP-1 Obstruction Summary........................................................54 
Table 4.2-3      Burien Site BP-1 Obstruction Summary .......................................................56 
Table 4.3-1      SeaTac Site SC-1 Obstruction Summary........................................................59 
Table 4.3-2      SeaTac Site SR-1 Obstruction Summary........................................................62 
Table 4.3-3      Burien Site BR-1 Obstruction Summary .......................................................65 
Table 4.3-4      Des Moines Site DR-1 Obstruction Summary...............................................67 

List of Figures 
Figure 1     Project Vicinity Map 
Figure 2     Location of Obstructions
Figure 3     Site P-1 Access, Staging, and Site Preparation Plan
Figure 4     Site P-1 Obstruction Removal and Disposal Plan 
Figure 5     Site P-1 Planting Plan 
Figure 6     Site P-2 Access, Staging, and Site Preparation Plan
Figure 7     Site P-2 Obstruction Removal Plan 
Figure 8     Site P-2 Planting Plan 
Figure 9     Sites P-3a & P-3b Access, Staging, and Site Preparation Plan
Figure 10    Sites P-3a & P-3b Obstruction Removal Plan 
Figure 11    Sites P-3a & P-3b Planting Plan 
Figure 12    Site P-4 Access, Staging, and Site Preparation Plan
Figure 13    Site P-4 Obstruction Removal and Disposal Plan 
Figure 14    Site P-4 Planting Plan 
Figure 15    Site P-5 Access, Staging, and Site Preparation Plan 
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Table of Contents 
Figure 16    Site P-5 Obstruction Removal Plan 
Figure 17    Site P-5 Planting Plan 
Figure 18    Site P-6 Access, Staging, and Site Preparation Plan
Figure 19    Site P-6 Obstruction Removal and Disposal Plan 
Figure 20    Site P-6 Planting Plan 
Figure 21    Obstruction Management Phasing Plan 

List of Appendices 
Appendix A     Approved Vegetation List 













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LIST OF ACRONYMS AND ABBREVIATIONS 
ALSF           approach lighting system with flashing lights 
AOA         Air Operation Area 
BMP          best management practice 
Port              Port of Seattle
Program         Flight Corridor Safety Obstruction Management Program 
ROW        right-of-way 
SR             State Route 
STIA           Seattle-Tacoma International Airport 
WSDOT       Washington State Department of Transportation 












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LIST OF SPECIES NAMES
Common Name                Latin Name 
American linden                   Tilia americana 
Apple                          Malus sp. 
Big-leaf maple                       Acer macrophyllum 
Bitter cherry                         Prunus emarginata 
Black cottonwood                   Populus balsamifera 
Black locust                         Robinia pseudoacacia 
Common holly                   Ilex aquifolium 
Common laurel                   Prunus laurocerasus 
Deodar cedar                      Cedrus deodara 
Douglas fir                          Pseudotsuga menziesii 
English ivy                         Hedera helix 
Giant sequoia                       Sequoiadendron giganteum 
Himalayan blackberry                Rubus ameriacus 
Japanese maple                     Acer palmatum 
Lombardy poplar                   Populus nigra 
Mountain ash                     Sorbus sp. 
Pacific madrone                     Arbutus menziesii 
Paper birch                        Betula papyrifera 
Pine                            Pinus sp. 
Red alder                          Alnus rubra 
Western red-cedar                   Thuja plicata 
Scotch broom                     Cytisus scoparius 
Scots pine                          Pinus sylvestris 



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1  INTRODUCTION 
As a condition of the Federal Aviation Administration-issued Airport Operating Certificate,
the Port of Seattle (Port) is required to ensure there are no obstacles or obstructions on or
around the Seattle-Tacoma International Airport (STIA) that could affect aviation safety. In
2014, the Port conducted a comprehensive obstruction analysis that used Light Detection and
Ranging (LiDAR) remote sensing and imaging technology to identify obstructions that extend
into, or very near (within a 6-foot threshold of), navigable airspace. In 2015, the obstruction
quantities identified through this analysis were refined through a ground-truthing field
exercise. The field reconnaissance also characterized the obstructions by species type and size
(stem diameter and estimated height). On Port sites, the reconnaissance also identified future
obstructions, and where applicable, quantified the understory trees that would be removed or
impacted during removal activities. Overall the process has identified 2,747 trees
(1,799 obstructions and 948 non-obstruction understory features) for removal. The purpose of
this report is to provide a detailed methodology and timeline for management of obstructions
on Port, public, and private properties surrounding STIA.
1.1   Components of Implementation Plan 
This report includes an introduction to the sites that have been identified; a characterization
of obstructions and potential obstructions; a discussion of obstruction management methods;
site plans that describe how these methods should be applied to these various Port, public,
and private sites; cost estimates that can be used for budget planning; and a detailed schedule
for implementing the Flight Corridor Safety Program (Program).
1.2   Overview of Port, Public, and Private Sites 
Obstructions occur on Port, state, city, and private commercial and residential parcels. The
following section introduces the grouping of these parcels into 14 discrete sites. See Figure 1
for a project vicinity map. 



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Introduction 
1.2.1    Port Sites 
Obstructions on Port property (shown in Figure 2) have been grouped into the following
seven sites based on geographic location, site conditions, and access considerations:
Site P-1 is the only site located north of STIA. This site includes obstructions within
a steep slope sensitive area. 
Site P-2 is located west of STIA near the Port's west side office. The majority of the
obstructions within this site are outside of sensitive areas, though several obstructions
are within wetland buffers or on steep slopes.
Site P-3 (P-3a and P-3b) is located south of STIA and north or northeast of
Des Moines Creek. Many obstructions in these sites are within wetlands, wetland
buffers, stream buffers, or on steep slopes.
Site P-4 is located south of STIA and south or southwest of Des Moines Creek.
Obstructions on this site are all outside of sensitive areas. The obstructions at the
south end of this site are within a parcel that includes trails used by the public. 
Site P-5 is located south of STIA, and is a forested parcel that includes walking and
biking trails used by the public. Some obstructions on this site are within steep slope
sensitive areas.
Site P-6 is located south of STIA and north of Des Moines Creek, within the Tyee
mitigation site. The majority of obstructions within this area are within wetlands or
wetland buffers. 
1.2.2    Public Sites 
Obstructions on public property (shown in Figure 2) have been grouped into the following
three sites based on property ownership (school district property is presented by the city
jurisdictions they fall within):
Site WP-1 is located within the city of SeaTac, and includes both active right-of-way
(ROW) and unconstructed ROW owned by the Washington State Department of
Transportation (WSDOT). The site includes areas to the west and southwest of STIA. 
The obstructions on this site are all outside of sensitive areas.
Site SP-1 includes publically owned utility, ROW, natural resource, and school
district sites in the city of SeaTac. This site includes two locations, one of which is

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Introduction 
located north of STIA, the other located southwest of STIA. The southwest area
includes wetland and wetland buffer sensitive areas. 
Site BP-1 includes publically owned ROW within the city of Burien. This site is
located northwest of STIA. These obstructions are all outside of sensitive areas. 
1.2.3    Private Sites 
Obstruction sites on private property (shown in Figure 2) have been grouped into the
following four sites, based on local jurisdiction and type of land use (Commercial/Institutional
versus Residential):
Site SC-1 is located in the city of SeaTac and includes commercial lots owned by
Boeing (one parcel), commercial lots owned by car rental companies (three parcels),
and one church institutional site (one parcel). This site includes two locations, one of
which is located northeast of STIA, the other located southwest of STIA. The
southwest area includes wetland and wetland buffer sensitive areas. 
Site SR-1 includes 32 private residential properties within the city of SeaTac, located
to the northeast and southwest of STIA. These obstructions are all outside of sensitive 
areas. 
Site BR-1 includes 17 private residential properties within the city of Burien, located
to the northwest and southwest of STIA. These obstructions are all outside of
sensitive areas. 
Site DR-1 includes 25 private residential properties within the city of Des Moines,
located to the southwest of STIA. A portion of this site is located within wetland and
wetland buffer sensitive areas. 





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2  OBSTRUCTION INVENTORY
Table 2.1 provides a summary of existing and potential obstructions for different types of
property ownership within three local jurisdictions. The presence of sensitive areas
(wetlands, wetland buffers, stream buffers, and steep slopes) in proximity to obstructions is
also identified. Figure 2 illustrates the location of these obstructions within the three local
jurisdictions. 














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Obstruction Inventory 
Table 2.1
Obstruction Removal Summary by Location 
Obstruction Removal                        Understory
Jurisdiction               Existing      Potential      Total      Obstructions Within Sensitive Areas       Tree     Total Trees
Property Ownership    Obstructions1   Obstructions2  Obstructions    Existing    Potential     Total3     Removal    Removed 
City of SeaTac 
Port                   362         478         840         149        238        387        327        1,167
WSDOT            484       119       603       0       0       0      6214     1,224 
Public                   87           41          128          4         11         15          0         128 
Residential              46           22          68          0         0         0         0         68 
Commercial/Religious       22          22         44         2         5         7         0         44 
Subtotal               1,001         682        1,683                          409       948       2,631 
City of Burien 
Public                   6           0           6          0          0          0          0          6
Residential              58           14          72          0         0         0         0         72 
Commercial           0          0         0        0        0        0        0        0 
Subtotal                64          14          78                             0         0        78 
City of Des Moines 
Public                   0           0           0          0          0          0          0          0
Residential               16           22          38          1         1         2         0         38 
Commercial             0          0         0         0         0         0         0         0 
Subtotal                16          22          38                             2         0        38 
Total      1,081         718         1,799                             411        948        2,747 
Notes: 
1. Existing obstructions are trees that are currently within the navigable airspace for STIA.
2. Potential obstructions are trees that are predicted to enter the navigable airspace within 5 years.
3. Totals are adjusted to reflect the actual number of tree obstructions within sensitive areas, and remove double counting (e.g., individual trees that are
within both steep slope and wetland buffer areas).
4. Estimated understory quantity is preliminary and subject to change (derived from aerial photograph analysis).
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3  OBSTRUCTION REMOVAL AND SITE MANAGEMENT METHODS 
The methods for obstruction removal and site management are discussed here for the
following key implementation steps:
1.  Site preparation 
2.  Obstruction removal and material disposal 
3.  Site treatment
4.  Monitoring 

In addition, the best management practices (BMPs) that will be applied during
implementation are presented. The detailed implementation plans for individual sites
(provided in Section 4) will draw upon the methods and BMPs presented here. 
3.1   Site Preparation 
Site preparation activities prior to obstruction removal include verifying/inspecting site
conditions; identifying and installing access barriers, access routes, and staging areas;
identifying and installing erosion and sediment control measures; salvaging vegetation; and
marking obstructions and other features to be removed.
3.1.1    Site Visit 
Before any site work commences, a site visit will be held with both the contractor and Port
engineer in order for the contractor to verify the following:
Hazardous features of the site: Permanent features should be marked/flagged to
protect site personnel, biological hazards (e.g., unsanitary conditions, discarded
syringes) should be identified and removed.
Site access issues: Traffic control measures may be required for sites along busy or
congested public ROWs.
Utilities in need of protection: Stormwater and electrical utilities, including large
stormwater ponds, will likely be the main utilities that will require protection.
However, any sites that will require excavation for obstruction removal will also
require a utility location/verification through the Utility Notification Center.
Existing facilities in need of protection: These features could include STIA features such
as the Air Operation Area (AOA) perimeter fence, the Port's west side office, or supports
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Obstruction Removal and Site Management Methods 
for runway approach lighting systems with flashing lights (ALSF). Existing facilities on
private sites include structures, grounds, and landscaping outside of the obstruction
removal area. Additional steel plates or mats and barricades will likely be required to
safely remove obstructions on private sites without impacting existing structures. 
Sensitive areas in need of protection: These features could include steep slopes,
wetlands, streams, and their buffers. In addition, topographic swales/ditches that
could direct additional stormwater or sediment-laden runoff to these sensitive areas,
and areas of potential erosion, should also be identified.
3.1.2    Site Access and Safety 
Access barriers are necessary to control the site from trespass or unintentional entrance by
unauthorized personnel. While most Port sites have adequate access control from existing
fencing, the more congested Site P-2, near the Port's west side office, will need to be barricaded.
Additionally Port sites that currently host informal public access will require access control
measures. Temporary chain-link fencing, with 20-foot-wide lockable gates along the
construction equipment access route(s), can provide a suitable barrier. Small public or private 
sites, or those along roadways, may require additional signs, barricades, or competent flagmen to
ensure the public is protected from hazards associated with tree removal. 

Access and exit points should be limited to one route, if possible. This truck or equipment
driveway should be stabilized to avoid tracking sediment on adjacent roadways. Stabilization
can include placing a minimum 12-inch layer of 4- to 8-inch-sized quarry spalls over
geotextile fabric, for a length of 25 feet and width of at least 15 feet. Longer access routes
into a site may be required depending on the substrate/groundwater site characteristics and
the size and weight of equipment used; pads of quarry spalls and geotextile can also be used
for this application.
3.1.3    Clearing Limits and Tree Marking 
Prior to obstruction removal, clearing limits will be marked with fencing. The trees that will
be removed should be confirmed and marked in multiple places on the trunk. This process is
an important extra security step to make sure that only the intended trees are removed.

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Obstruction Removal and Site Management Methods 
3.1.4    Erosion and Sediment Controls Installation 
Prior to obstruction removal, erosion and sediment controls will need to be planned and
installed. Planning items will include development of a spill prevention, control, and
countermeasures plan, and consideration of overall site layout during construction. Fuel
storage should be segregated from other materials and located at least 20 feet from streams and
wetlands. The fuel storage area must be graded to ensure containment of any leaks or spills. 
3.1.5    Plant Salvage  Optional Action 
Through community service events, or partnering with native plant organizations, the Port
may salvage native shrub and groundcover plant materials within the obstruction removal
clearing limits for reuse. Plant materials should be carefully stockpiled for later relocation,
exercising care when moving the plant materials to avoid breaking branches or roots.
Salvaged vegetation may be used within cleared areas during the site treatment step in the
process. This vegetation may also be used on other Port properties, or provided for
restoration work by other agencies (e.g., King County, EarthCorp).
3.2   Tree Obstruction Removal and Material Disposal 
3.2.1    Tree Removal and Clearing Methods 
Obstruction removal methods and equipment vary depending on site characteristics, the
distribution and characteristics of obstructions on a site, and the type of disposal method or 
sale of the cleared material. The range of tree removal and clearing methods, and their
suitability, are summarized in Table 3.2-1, followed by a more detailed discussion.





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Obstruction Removal and Site Management Methods 
Table 3.2-1
Summary of Obstruction Removal and Clearing Methods 
Method 
Description                                    Suitability 
Clearing and Grubbing 
Clearing involves removal of trees and vegetation, including    Suitable for areas with dense
invasive species, as well as other understory and groundcover   obstruction groupings where adjacent
vegetation above the soil surface. Fell and limb trees using     areas are not congested or major traffic
mechanical equipment such as a feller buncher; harvester     corridors 
equipment may also buck the logs into smaller pieces.
Remove invasive species as well as other understory and
groundcover vegetation. Grubbing a cleared area entails
removing organic matter in the soil, often to a minimum of
12 inches in depth, provides an opportunity for stripping
topsoil to be used in future restoration planting efforts.
Salvaged topsoil can be segregated and stockpiled separately
from other cleared material; it can be spread over disturbed
areas upon completion of obstruction removal activities. 
Tree Removal (excludes stump grubbing) 
Fell, limb, and buck trees using mechanical means and/or     Suitable for areas with dense
chain saws (manual) as needed. Remove invasive species, and  obstruction groupings where adjacent
retain, as practical, the remaining understory.              areas are not congested or major traffic
corridors, and where full stump removal
(grubbing) is not required 
Selective Clearing and Tree Removal (manual work) 
Fell, limb, and buck trees using chain saws. Remove invasive   Suitable within or near sensitive areas,
species, but retain remaining understory.                 and/or where isolated obstructions
occur, particularly on congested sites 
Retain Stumps 
Follow tree removal or selective removal of trees, which leaves  Suitable where isolated or small
a 1- to 2-foot stump above the ground surface. To inhibit      groupings of obstructions occur, and
resprouting, stumps can be treated using broad-spectrum     retaining stumps is used to protect
glyphosate or fungus (mycilia) tablets that encourage fungus   sensitive areas like steep slopes or
to eat away at the remaining structure.                  wetlands 
Remove Stumps 
Cut or grind and mulch stumps, and the associated root mass   Suitable on sites outside of sensitive
below the ground level, using a stumper or stump grinder     areas 
attachment. Another option is to use a grubbing blade
mounted on the front of a carrier vehicle, or cut a tree
part-way down and push it over (clearing and grubbing
operation). 

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Obstruction Removal and Site Management Methods 
Tree removal could take the form of selectively removing trees with a chain saw or using
mechanical means. Manual removal involves felling, limbing, and bucking trees using
chain saws. A site that is congested and/or contains many existing facilities or grounds to be
preserved, or is inaccessible to large equipment, will require manual methods of removal.
Selective removal within the Port Site Plans denotes manual removal methods for felling
trees; all other removal methods will involve mechanical felling operations.

Mechanical felling has worker safety, productivity, and efficiency benefits compared to
manual removal; however, this method is infeasible for certain sites where equipment cannot
fit, or where equipment would damage existing facilities or impact sensitive areas. Where
feasible, mechanical felling is the best option for preparing timber for sale, which is an
obstruction "disposal" option for many of the Port and WSDOT sites for this Program.

Common equipment used for large mechanical felling operations includes the following:
Feller buncher, which has motorized vehicle base (tracked or wheeled) with a head
that can cut and gather several trees at once; the most common tracked
feller bunchers in the western United States are 12 feet wide, with excavator bases
and swing booms with a 25-foot reach (USDA 2016)
Delimber, which is used to remove branches from felled trees 
Harvester, which consolidates felling, delimbing, and bucking (cutting tree into
appropriate lengths) into one machine 
Skidder, which is used to bundle and pull logs out of a forest 
Forwarder, which is a vehicle that uses a boom arm to load and carry logs out of the
forest clear of the ground 

Stump removal can occur through the use of a grubbing blade (for clearing and grubbing
operations) that can be mounted on the front of a carrier vehicle. Using this method, or
cutting a tree part-way down and pushing it over, is an option to harvest material for large
woody debris applications for restoration projects. Another option for stump removal is to
cut or grind and mulch stumps, and the associated root mass below the ground level, using a
stumper or stump grinder attachment. Grinding stumps can lead to sinkholes and grade
irregularities when the remaining root systems decompose overtime. These grade
irregularities are not an issue within natural forested areas, but they do have moderate safety
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Obstruction Removal and Site Management Methods 
implications on sites used by the public. Within private sites and recreation areas, grubbing,
rather than grinding of stumps, is recommended. 

Grubbing a clearing area (i.e., removing organic matter in the soil, often to a minimum of
12 inches in depth), provides an opportunity for stripping topsoil to be used in future
restoration planting efforts. Salvaged topsoil should be segregated and stockpiled separately
from other cleared material; it can be spread over disturbed areas upon completion of
obstruction removal activities. If a site will not support future planting, topsoil can
alternatively be transported to other sites for use in restoration and revegetation efforts. 

Areas within sites that are on steep slopes or in wetlands will benefit from retaining stumps
after tree removal in order to stabilize soils and minimize impacts to these sensitive areas. To
inhibit resprouting, stumps can be treated using broad-spectrum glyphosate, or using fungus
(mycilia) tablets that encourage fungus to eat away at the remaining structure. 

Erosion and sediment control measures will need to be actively managed during the
obstruction removal phase of the Program. If monitoring or inspection shows that the
control measures are ineffective, repairs should be made or replacement measures should be
installed. If sediment reaches one-third of the exposed height of the control measure, the
sediment should be removed and disposed of properly.
3.2.2    Material Disposal Options 
Options for disposal of cleared obstructions, potential obstructions, and associated vegetation
(e.g., invasive species, vegetation impacted during removal) are summarized in Table 3.2-2,
followed by a more detailed discussion.




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Obstruction Removal and Site Management Methods 
Table 3.2-2
Summary of Material Disposal Methods 
Method 
Description                                        Suitability 
On-site Disposal (including chipping and mulching) 
Leave cleared materials on site with minimal processing, though     Suitable for most sites (with
cutting large tree pieces into manageable log segments may be      owner's permission), outside of
required. Alternatively, material may be processed into wood       wetlands 
chips/mulch, which can provide benefits to the site through invasive 
species control and soil nutrient inputs.
Off-site Disposal 
Remove material from site and dispose at an approved location, or   Suitable for wetland areas where
to a beneficial reuse site identified by the Port.                   on-site disposal is not feasible, or
other sites at owner's discretion 
Timber Sale 
Establish board foot volumes, market, and prepare trees for sale.     Large, forested tracts with
merchantable timber 

3.2.3    On-site Material Disposal 
Cleared materials may be left on site with minimal processing, though cutting large tree
pieces into manageable log segments may be required. Alternatively, material may be
processed into wood chips/mulch, which can provide benefits to the site through invasive
species control and soil nutrient inputs. For small diameter trees, this mulching option can
be combined with the obstruction removal step through the use of a mechanical mulcher.
Disposing of material on site is not suitable for non-Port sites unless permission for this
disposal method is approved by the owner. Disposing of material within wetland areas is also
prohibited as this material could be interpreted as wetland fill. 
3.2.4    Off-site Material Disposal 
Cleared material may be disposed of off site through the contractor taking ownership of the
material and disposing of it at an off-site, permit-compliant location of their choosing. 
Alternatively, the Port may wish to take ownership of some of the cleared obstruction
material for beneficial uses in other Port locations as restoration (e.g., large woody debris) or
site furnishings (e.g., log edging, seating, art features). This Port beneficial reuse option can

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Obstruction Removal and Site Management Methods 
be facilitated by identifying this material on site and specifying a location where the
contractor can deliver the material to be stockpiled. 
3.2.5    Marketing and Selling Timber 
The Port and WSDOT may consider a timber sale as another option for material disposal.
This option could provide significant revenue, but it also requires additional planning steps. 
Generally the timber selling process would include the following:
Researching the timber market condition and trends as they relate to desired species,
minimum quantities, sizes, and material quality 
Refining a tree inventory in order to project the available timber volumes 
Developing a marketing strategy, guided by the following questions: 
What are the products and when will they be available? 
How will products be sold (stumpage [i.e., standing timber] or as logs)?
What is the current market value for these products? 
Who are the potential buyers? 
Clearly laying out property lines of sale area and marking timber 
Promoting the products through actively contacting potential buyers and providing a
prospectus 
Evaluating offers and drawing up a timber sale contract, and a logging contract for log
products 
Actively monitoring the operation 
3.3   Site Treatment 
Site treatment following obstruction removal will involve stabilizing soils using vegetation
and, in certain instances, geotechnical methods. Closeout of the work will include removing 
temporary facilities and erosion/sediment control measures, and cleaning up the site. 
3.3.1    Planting Bed Preparation 
Soil preparation and the installation of erosion control fabrics (if warranted) will precede plant
installation tasks. Soil amendment may be needed for areas with compacted soil or areas

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where an excessive amount of topsoil was removed through obstruction removal operations. 
Soil amendment can be placed in planting areas and rototilled into the existing subgrade. 

The installation of jute matting is recommended for sites with slopes greater than 4:1 
(4 horizontal to 1 vertical) to control slopes during plant establishment. This material
consists of unbleached, single jute yarn, which is woven into a mat. Jute matting is installed
by rolling out the fabric and, where multiple strips of mat are required, overlapping adjacent
mats by a minimum of 4 inches. The upslope end of the mat is secured by burying and
staking the ends in a trench and then backfilling the trench. The matting is further secured
with wooden stakes spaced every 2.5 feet along the length of the material.
3.3.2    Plant Installation 
Plant installation should be performed within the wet season if possible (between October
and May) unless an irrigation system is available. The specific plant species recommended 
for each of the Port sites are identified on the plant schedules provided in Figures 5, 8, 11, 14,
17, and 20. For non-Port sites, Appendix A provides a list of replacement tree species with
mature tree heights that are well below obstruction levels.

Plant materials for Port properties can be supplemented with salvaged material removed
during site preparation activities. Purchased plant materials can include both
container-grown stock and livestake cuttings. Container-grown stock should be inspected
prior to installation to ensure plants meet the following standards:
Neither overly loose in the container with underdeveloped root systems, nor
container bound 
Free of weeds, disfiguring knots, injuries/abrasions, and all forms of infestation 

Trees that are installed in public spaces and ROWs are generally higher grade material, and
must meet location jurisdiction requirements (Burien Code Chapter 19.25, Interlocal
Agreement Landscape Design Standards, SeaTac Development Standards Chapter 15.445).
Within applicable sites in the cities of SeaTac and Burien, these requirements include the
following:
Deciduous trees shall have a caliper of at least 1.75 inches (Burien) or 2 inches (SeaTac) 

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Evergreen trees shall be at least 6 feet (Burien) or 8 feet in height (SeaTac) 

Additional requirements may include the following:
Conifer trees should have only one leader (growing apex) 
Deciduous trees that have a solitary leader shall have only lateral branches thinned by
pruning 
Pruning requirements for low branches for accessibility on sidewalks and clear sight
distances (branches typically pruned 5 to 8 feet above ground level) 

Container plants should be installed according to the following requirements: 
Remove plants from containers in a manner that prevents damage to their root
system. Containers may require vertical cuts down the full depth of the container to
accommodate removal. All circling roots shall be loosened to ensure natural
directional growth after planting. 
Install plants within pits that are sized at least twice the diameter of the root system
or container, with scarified sides and bottom. 
Set plant material in the planting pit to proper grade and alignment. Set plants
upright, plumb, and faced to give the best appearance or relationship to each other or
adjacent structure. Set the crown of plant material at the finish grade. No filling will
be permitted around trunks or stems or above grafts on grafted trees.
After plants are set, water in soil mixture around bases of root balls and fill all voids. 
Mulch shrub beds immediately after planting. Thoroughly water mulched areas.
After watering, rake mulch to provide a uniform finished surface. Mulch shall be
feathered back from base of trees and shrubs to reduce potential plant rot. 

Livestake cuttings are live plant materials without a previously developed root system; this
type of material is often used for willow installations within moist areas, livestake
installation is not suitable for non-irrigated, dry soils. The source material for livestakes
should be dormant when the cuttings are made, and cut from material on a plant that is
1 to 2 years old. Cuttings can only be stored for 2 weeks (kept moist and shaded) before
installation. Installation during fall to early spring (October 15 to March 15) is
recommended. The top cut for the stake should occur immediately above a bud. The lower
root end shall be cut at about a 45-degree angle. Livestake cuttings should be cut and
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installed with the bark intact, but with no other branches or stems included. Prior to
installation, the stakes should be soaked continuously. 

Livestake plants should be installed according to the following requirements: 
Pound livestakes into the ground with a mallet or create a hole using a pilot bar in
firm soils 
Plant at least 80% of the stake length within the ground and ensure that two to five 
bud scars are present above the ground 
Tamp soil around the stake 
Mulch the livestake planting area and thoroughly water mulched areas 
3.4   Monitoring 
Where black cottonwood or maple stumps remain (steep slopes and wetlands), they should be
monitored to ensure resprouting does not lead to future obstructions. Sprouts from stumps can
rarely achieve heights above 80 feet, but in certain areas near STIA, these sprouts may still
reach obstruction levels. Stumps can be treated using broad-spectrum glyphosate, or using
fungus (mycilia) tablets that encourage fungus to eat away at the remaining structure. 

Long-term monitoring will be required to document potential future obstructions and
provide regular maintenance of areas with low-height obstructions. Monitoring will occur
for two years on all sites to ensure revegetation mitigation measures meet performance
standards below. If monitoring reveals that the revegetation mitigation measures are not
meeting the performance standards, corrective action will occur in accordance with SeaTac
Municipal Code 15.700.120 as follows: 
Performance Standard 1: Average survival of all native planted stock will be 100% at
the end of Year 1 and at least 80% at the end of Year 2. 
Performance Standard 2: Invasive plant species are maintained at levels below
20% cover averaged over the entire obstruction removal area. 

Including a 1-year plant warranty requirement within the contract specifications is
recommended. This will require the Contractor to warrant plant materials to remain alive
and be in healthy, vigorous condition for a period of 1 year after the date of physical
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completion. The warranty will require replacement of plants that are dead or in unhealthy
conditions. Typically plant warranties do not include damage or loss of plants caused by
fires, floods, freezing rains, lighting or wind storms, extreme winter weather conditions,
vandalism, or negligence on the part of the Owner.
3.5   Erosion and Sediment Control Best Management Practices
A construction stormwater pollution prevention plan and erosion and sediment control
measures will be required to control the quantity and quality of stormwater that may pass
through the obstruction management sites. The regulatory memorandum provides detail on
the construction stormwater general permit associated with this work. This section outlines
the most appropriate BMPs that can be used during obstruction management
implementation. More detail on the BMPs identified here is available through the 
Stormwater Management Manual for Western Washington (Ecology 2012).
3.5.1    Preserve Vegetation/Mark Clearing Limits 
Natural vegetation and the duff layer/native topsoil outside of the obstruction removal zones
should be protected as these materials not only provides long-term ecological function, but
also control stormwater erosion. Clearly marking the limits of clearing will ensure this
material is not mistakenly removed during construction activities. Appropriate BMPs for
this element include the following:
BMP C101: Preserving Natural Vegetation 
BMP C102: Buffer Zones
BMP C103: High Visibility Fence 
3.5.2    Establish Construction Access 
Constructing a clear construction access and exit location provides safety benefits (e.g., clear
understanding of vehicle traffic), and also provides an opportunity to control sediment from
being tracked outside of the construction site. Appropriate BMPs for this element include 
the following:
BMP C105: Stabilized Construction Entrance/Exit
BMP C107: Construction Road/Parking Area Stabilization 
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3.5.3    Install Sediment Controls 
Earth moving on a construction site increases the risk of sediment being washed
"downstream" and, in turn, impacting adjacent sites and/or sensitive areas such as wetlands
or streams. Sediment control measures trap sediment on site where it can be managed.
Appropriate BMPs for this element include the following:
BMP C233: Silt Fence
BMP C234: Vegetated Strip
BMP C235: Wattles
3.5.4    Stabilize Soils and Protect Slopes 
Soil that has been worked can be protected from erosion and sedimentation by soil
stabilization measures. Soils must not remain exposed and unworked for more than 7 days
during the dry season (May 1 to September 30), or for more than 2 days during the wet
season (October 1 to April 30). Appropriate BMPs for this element include the following:
BMP C120: Temporary and Permanent Seeding 
BMP C121: Mulching
BMP C122: Nets and Blankets
BMP C123: Plastic Covering
3.5.5    Maintain Best Management Practices and Manage the Project 
Managing the project will include accounting for the dry and wet seasons as they relate to
the construction schedule. During construction, a designated Certified Erosion and Sediment
Control Lead person will lead the inspection and monitoring of BMPs, and will work with
the contractor to improve BMP performance over the life of the project. Appropriate BMPs
for this element include the following:
BMP C160: Certified Erosion and Sediment Control Lead
BMP C162: Scheduling


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4  SITE PLANS 
This section provides detailed obstruction removal and revegetation methods for the
Program. A summary of the quantities of tree removal and replacement for the different
property types is shown in Table 4.1-1. The required tree planting quantities are based on
revegetation ratios, which vary based on jurisdiction requirements. 

Table 4.1-1
Summary of Tree Removal and Replacement Quantities  All Sites 
Jurisdiction               Total      Understory   Total Trees   Required Tree
Ownership         Obstructions    Removal    Removed    Replacement 
City of SeaTac 
Port                  840         327        1,167        1,4892 
WSDOT            603       6213      1,224      1,2244 
Public                  128          0         128          143 
Residential              68           0           68          68 
Commercial/Religious      44          0         44         51 
Subtotal              1,683        948        2,631        2,975
City of Burien 
Public                  6           0          6          18 
Residential              72           0           72          72 
Commercial            0         0         0         0
Subtotal               78          0          78          90 
City of Des Moines 
Public                  0           0          0           0 
Residential              38           0          38          40 
Commercial            0         0         0         0
Subtotal               38          0          38          40 
Total     1,799         948        2,747        3,105
Notes: 
1.  Required tree replacement quantities based on mitigation ratios established by the Port and local
agencies. Actual tree replacement quantities may exceed the required ratios. 
2.  See Table 4.1-2 in Section 4.1 for more information on tree replanting for Port properties.
3.  Estimated understory quantity is preliminary and subject to change (derived from aerial photograph 
analysis). To be confirmed with WSDOT, the replacement requirement may be as large as 4:1 ratio.


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Site Plans 
4.1   Port Properties 
The Port properties include seven sites requiring removal of existing obstructions and future
obstructions. These sites are to the north, west, and south of STIA. Access to five of the sites
is actively controlled by the Porteither because they are located in close proximity to
active Port operations (west side office) or they occur within Port property that is restricted
from public use and fenced. Two of the sites contain areas accessible by the public for
recreational use. A summary of tree removal and replacement for Port sites is presented in
Table 4.1-2.

Table 4.1-2
Summary of Tree Removal and Replacement  Port Sites 
Trees
Total     Understory   Total Trees   Required Tree   Replaced   Trees Replaced
Port Site   Obstructions    Removal      Removed    Replacement    Within Site    Outside of Site 
P-1         56          0         56         56         41         15 
P-2        239         0         239        290         16         274 
P-3a         247          0         247 
551        310         241 
P-3b         51          0         51 
P-4           95            0            95           95           198          -103 
P-5        134        327        461        461         92         369 
P-6         18          0          18         36         48         -12 
Total      840         327         1,167        1,489        705          784
4.1.1    Site P-1
4.1.1.1     Site Description 
This 2.5-acre site is the only Port site located north of STIA, and includes a wetland, wetland
buffer, and steep slopes. In addition to 5 tree obstructions and 51 potential tree obstructions,
the site contains invasive species (including English ivy, common holly, and Himalayan
blackberry). The site contains artificial fill, predominately within the sloped areas, which
includes plastic barrels, riprap, concrete rubble, and potentially sharp, steel construction waste. 


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Site P-1 Overview Diagram 







Site P-1 Representative Site Photographs



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Table 4.1-3
Port Site P-1 Obstruction Summary 
Species            Quantity         Diameter at Breast Height       Estimated Height 
Existing Obstructions (5 total) 
Black cottonwood     5            28  37"                  125  140' 
Potential Obstructions (51 total) 
Black cottonwood     26            6  55"                   20  140' 
Cluster 1: 10 trees   Cluster 1: 8" 
Red alder                                                 Both clusters: 25' 
Cluster 2: 15 trees   Cluster 2: 9" 
4.1.1.2     Site Implementation Plan 
Access and Construction Staging (Figure 3)
Site P-1 can be accessed from the north via Highway 518 East, which will require a
temporary access agreement through WSDOT ROW.

An area suitable for construction staging to support work at Site P-1 is located adjacent to the
eastern portion of the site. This area is located near a stormwater retention basin, which
must be protected. The staging area and access route from Highway 518 would need to be
restored to pre-project conditions following obstruction removal work. 

Site Condition Review 
1.  Site P-1 hazards include steep slopes, with a number of obstructions located on slopes
up to 35 degrees. In addition, artificial fill with potentially sharp materials and
thorny invasive plants constrain access.
2.  Sensitive areas that will be encountered on the site consist of steep slopes. Sensitive
areas adjacent to the site to the west include a wetland and wetland buffer. While
roads are present to the west of the site (within the wetland buffers), no access from
these roads will be permitted in order to protect the wetland and wetland buffers.
3.  Stormwater outfalls discharge water at the south and northeast corners of Wetland 3. 
No work or staging is permitted on this side of the site. 
4.  ALSF structures are present to the west of the site. No work or staging is permitted
on this side of the site. 
5.  Other STIA-related infrastructure to be protected includes one stormwater retention basin. 
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Site Preparation (See Figure 3)
1.  Secondary access improvements: Access to the site will require cutting through brush
and placing a base material for access from Highway 518. 
2.  Sensitive area protection: Install sediment controls downstream of the work area and
outside of the wetland boundary.
3.  Infrastructure protection: Protect the culvert that transports water from the east to
west wetland complex by ensuring sediment control measures are in place prior to
commencing obstruction removal site work. Biodegradable silt fencing is
recommended as it can be left in place, further minimizing wetland impacts following
projection completion. 
4.  Geotechnical investigation: Further geotechnical evaluation for stability may be
needed prior to obstruction removal on steep slopes. This investigation may prescribe
slope stability mechanisms that are more conservative (e.g., armoring) than the
geotechnical fabric application presented below. 

Obstruction Removal and Material Disposal (See Figure 4)
1.  Remove and retain stumps of all black cottonwoods (5 obstructions, 26 potential
obstructions).
2.  Clear two clusters of 25 total red alder potential obstructions; these clusters are on
steep slopes. Retain all stumps. 
3.  Clear invasive species (English ivy, common holly, and Himalayan blackberry) within
clearing limits shown in Figure 3.
4.  Dispose of material by chipping and mulching, and placing processed material on site 
(outside of the wetland). Removed black cottonwood trees may provide
merchantable timber for fiber; however, removing the material unprocessed from this
site using a cable-logging operation, would increase cost, and the necessary cranes and
cables would penetrate the navigable airspace.

Site Treatment (See Figure 5)
The objective of site treatment measures is to control establishment of future obstructions,
stabilize slopes and soil disturbed by obstruction removal, and replace trees on site to the
extent possible. 
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Site Plans 
1.  Drill and treat stumps that remain with broad-spectrum glyphosate or fungus
(mycilia) tablets in order to discourage sprouting. 
2.  Install geotechnical fabric (jute) in all cleared areas with slopes greater than 4:1 prior
to revegetation efforts. 
3.  Revegetate cleared areas per the planting plan and planting schedule (Figure 5). The
planting categories allow for the following maximum heights for installed vegetation,
though species selected for each category were selected to grow far below the 
following thresholds: 
a.  Short height upland planting: 100 to 140 feet 
b.  Shrub upland planting: 80 to 100 feet 
c.  Groundcover planting: 40 to 80 feet
4.  The required tree replacement quantity associated with obstruction removal from
Site P-1 is 56 trees, with 41 trees planted within the site, and 15 trees planted on
other Port sites or another location within the drainage basin..
5.  The estimated planting quantities on Site P-1 will include the following:
a.  Trees planted on site: 41
b.  Shrubs: 1,600
c.  Groundcovers: 2,000
d.  Seeded areas: 37,500 square feet 

Monitoring 
1.  Monitor stumps and treat with broad-spectrum glyphosate or fungus (mycilia) tablets 
to control resprouting. While black cottonwood sprouts from remaining stumps are
unlikely to exceed 100 feet in height, these sprouts may still become future
obstructions within the higher topography areas of the site.
2.  Monitor for future obstructions.
3.  Monitor to ensure revegetation areas meet the following performance standards: 
a.  Performance Standard 1: Average survival of all native planted stock will be
100% at the end of Year 1 and at least 80% at the end of Year 2. 
b.  Performance Standard 2: Invasive plant species are maintained at levels below
20% cover averaged over the entire obstruction removal area. 

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Site Plans 
4.1.1.3     Best Management Practices 
The following BMPs are suitable measures for controlling sediment and erosion on Site P-1.

Table 4.1-4
Port Site P-1 Best Management Practices 
BMP Category          BMP Numbers and Titles 
Preserve Vegetation/Mark     BMP C101: Preserving Natural Vegetation 
Clearing Limits               BMP C102: Buffer Zones 
BMP C103: High Visibility Plastic, Metal, or Biodegradable Fence 
BMP C103: Silt Fence 
Establish Construction         BMP C105: Stabilized Construction Entrance/Exit 
Access                    BMP C107: Construction Road/Parking Area Stabilization 
Install Sediment Controls        BMP C235: Wattles 
BMP C233: Silt Fence 
Stabilize Soil and Protect        BMP C120: Temporary and Permanent Seeding 
Slopes                    BMP C121: Mulching 
Maintain BMPs and Manage    BMP C160: Certified Erosion and Sediment Control Lead 
the Project                  BMP C162: Scheduling 










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